Birds
Burrowing Owl (Athene cunicularia)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | 98 [64-132 (95% CI)] | Mean by 95% fixed-kernel | ha | M | Adult | 19 | Naval Air Station Lemoore | Exposure Factor Datasets | Fresno | USA |
Home Range | 189 [122-256 (95% CI)] | Mean by 100% MCP | ha | M | Adult | 22 | Naval Air Station Lemoore | Exposure Factor Datasets | Fresno | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation Table 1 | Number of individuals/706.5 ha | B | Juvenile | 946 territories in FL | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Dietary Composition | Rodentia: 74.9, Reptilia: 0.5, Anura: 3.9, Coleoptera: 12.2, Dermaptera: 0, Hymenoptera: 0.01, Ortoptera: 0.05, Aranea: 8.2, Scorpionida: 0.3, Gastropoda: 0 | % total biomass consumed | B | Not Reported | Inter-Andean Valley | Exposure Factor Datasets | ECUADOR |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.54 | Estimated percent survival | % | F | Adult | 65 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.12 |
Survival/ Mortality | 0.557 | Estimated percent survival | % | F | Adult | 63 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.071 |
Survival/ Mortality | 0.575 | Estimated percent survival | % | F | Adult | 85 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.065 |
Survival/ Mortality | 0.294 | Estimated percent survival | % | F | Adult | 64 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.053 |
Survival/ Mortality | 0.277 | Estimated percent survival | % | F | Juvenile | 65 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.1 |
Survival/ Mortality | 0.292 | Estimated percent survival | % | F | Juvenile | 63 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.056 |
Survival/ Mortality | 0.307 | Estimated percent survival | % | F | Juvenile | 85 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.053 |
Survival/ Mortality | 0.12 | Estimated percent survival | % | F | Juvenile | 64 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.025 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Dietary Composition | Mammals: 71.0, Birds: 1.4, Reptiles: 2.8, Invertebrates: 24.8 | % total biomass consumed | B | Not Reported | Pampa del Tamarugal, Atacama Desert | Exposure Factor Datasets | CHILE |
Dietary Composition | Mammals: 13.3, Birds: 0.3, Reptiles: 9.1, Invertebrates: 77.4 | % frequency | B | Not Reported | Pampa del Tamarugal, Atacama Desert | Exposure Factor Datasets | CHILE |
Dietary Composition | Mammals: 25.5, Birds: 7.7, Reptiles: 2.6, Invertebrates: 64.2 | % total biomass consumed | B | Not Reported | Pampa del Tamarugal, Atacama Desert | Exposure Factor Datasets | CHILE |
Dietary Composition | Mammals: 2.2, Birds: 0.7, Reptiles: 3.9, Invertebrates: 93.1 | % frequency | B | Not Reported | Pampa del Tamarugal, Atacama Desert | Exposure Factor Datasets | CHILE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|
Foraging Distance | 1762 | Distance moved from nest post-fledging | m | F | Juvenile | 21 | El Centro | Exposure Factor Datasets | Imperial | USA | 630 |
Foraging Distance | 397 | Distance moved from nest post-fledging | m | M | Juvenile | 8 | El Centro | Exposure Factor Datasets | Imperial | USA | 124 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Table 1 | Proporation of frequency of each taxon from pellets (temporal) | 35-110 | Somuncurá Plateau Protected Area | Exposure Factor Datasets | ARGENTINA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | 2010: 2,026 [1756-2336 (95% CI)] 2011: 2015 [1573-2317 (95% CI)] per 20,529 ha | Number of individuals/ha | Chihuahuan Desert | Exposure Factor Datasets | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Figures 1 & 2 | Mean proportion of prey in pellets | % | NR | Not Reported | 178 | South-eastern coast of Buenos Aires Province |
Exposure Factor Datasets | ARGENTINA |
Brown Pelican (Pelecanus occidentalis)
Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Hatching Success | 0 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.677 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.635 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.576 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.695 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.588 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.5 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Hatching Success | 0.537 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|
Population Density | See citation; fewer nests in ENSO years | Number of nests on islands of Gulf of Mexico 1970-2006 during ENSO/non-ENSO years | Gulf of Mexico | Exposure Factor Datasets | Breeding | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | 466 nests | Number of nests/>50,314 ha | Gulf of Chiriquí | Exposure Factor Datasets | PANAMA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|
Population Density | 0-910 | Number of individuals/90 sq km (temporal) | San Nicolas Island | Exposure Factor Datasets | Ventura | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|
Population Density | 2011: 88-289 2012: 120-1895 | Number of nests/583 sq km | 2-3 surveys/y | Small Islands of Bahía Santa María- La Reforma, Sinaloa, México |
Exposure Factor Datasets | CHILE | 2011 & 2012: 12-159 SE |
Time of Mating/ Laying | January | 2-3 surveys/y | Small Islands of Bahía Santa María- La Reforma, Sinaloa, México |
Exposure Factor Datasets | CHILE | ||
Population Density | Review | Number of nests in colonies that nest in mangroves | Small Islands of Bahía Santa María- La Reforma, Sinaloa, México |
Exposure Factor Datasets | CHILE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Population Density | 1722 | Number of individuals (area size NR) | Both Adults and Juveniles | 1722 | Three sites in Jacksonville, FL | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | Review | Number of individuals/sq km | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation | Number of breeding pairs (area size NR) | Adult | West coast US/Mexico border | Exposure Factor Datasets | Breeding | MEXICO |
Population Density | See citation | Number of individuals (area size NR) | Both Adults and Juveniles | West coast US/Mexico border | Exposure Factor Datasets | MEXICO |
American Kestrel (Falco sparverius)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Vertebrates (29.1 %) Arthropods (70.9 %) | Frequency determined by pellet analysis | Frequency, % | Fledgling | 19 fledglings | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA | |
Dietary Composition | Vertebrates (11.2 %) Arthropods (88.8 %) | Frequency determined by prey remains | Frequency, % | Fledgling | 19 fledglings | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA | |
Time of Mating/ Laying | Late October-late December | Adult | 6 nests | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA | |||
Clutch or Litter Size | 4.3 | eggs | Embryo | 6 nests | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA | 0.3 | |
Hatching Success | 0.73 | Embryo | 26 eggs | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA |
Bell's Vireo (Vireo bellii)
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|
Population Density | 0.01 | NR | Not Reported | NR | Missouri River between Pierre and Mobridge, SD |
Exposure Factor Datasets | USA | 0.01 |
Population Density | 0.02 | NR | Not Reported | NR | Missouri River between Pierre and Mobridge, SD |
Exposure Factor Datasets | USA | 0.02 |
Exposure Endpoint Type | Endpoint Value | Units | Life Cycle Stage | Location | Type | Error |
---|---|---|---|---|---|---|
Clutches or Litters per year | 2.29 | Clutches per female | Adult | Exposure Factor Datasets | 0.37 | |
Clutches or Litters per year | 7.07 | Eggs per female | Adult | Exposure Factor Datasets | 1.17 | |
Population Density | 1 | Number of territorial males per 10 ha | Adult | Exposure Factor Datasets | ||
Clutches or Litters per year | 2.02 | Clutches per female | Adult | Exposure Factor Datasets | 0.17 | |
Clutch or Litter Size | 6.49 | Eggs per female | Adult | Exposure Factor Datasets | 0.58 | |
Population Density | 1.06 | Number of territorial males per 10 ha | Adult | Exposure Factor Datasets | ||
Clutches or Litters per year | 1.47 | Clutches per female | Adult | Exposure Factor Datasets | 0.1 | |
Clutch or Litter Size | 4.88 | Eggs per female | Adult | Exposure Factor Datasets | 0.3 | |
Population Density | 1.19 | Number of territorial males per 10 ha | Adult | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Location | Type |
---|---|---|---|---|
Home Range | See citation text | Both Adults and Juveniles | San Joaquin River National Wildlife Refuge |
Exposure Factor Datasets |
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
ENDRIN | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | Toxicity Factor Datasets | USA | ||
MIREX | Not detected | Egg concentration | Embryo | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | ||
MERCURY COMPOUNDS | LCRS: 0.70, reference site: 0.10 µg/g ww | Brain concentration | Nestling | LCRS: 6, reference: 4 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 1.47, 2003: 3.39, 2004: 1.89 µg/g ww | Blood concentration | Not Reported | Nestling | 2002: 11, 2003: 31, 2004: 50 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 0.61, 2003: 0.64, 2004: 0.55 µg/g ww | Kidney concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
OXYCHLORDANE | MS-90: 0.0355, BI-82: 0.109, BI-89: 0.0153, BI-90: 0.0549, WM-89: 0.0241, WM-90: 0.0306, WM-91: 0.0204, SW-91: 0.0167 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
ZINC (elemental) | BI-89: 53.6, WM-89: 57.8, WM-91: 51.5, SW-91: 52.3 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
TOXAPHENE (POLYCHLORINATED CAMPHENES) | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | Toxicity Factor Datasets | USA | ||
PCB | 0.19 ppm ww | Egg concentration | Embryo | 3 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 5.86, reference site: 3.13 µg/g ww | Blood concentration | Adult | LCRS: 5, reference: 3 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 304, 2003: 359, 2004: 325 | Body weight | Not Reported | Nestling | 2002: 21, 2003: 32, 2004: 25 | Humboldt River | Toxicity Factor Datasets | USA |
METHYLMERCURY | 2002: 1.65, 2003: 1.90, 2004: 1.47 µg/g ww | Kidney concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
HEPTACHLOR EPOXIDE | MS-90: 0.0160, BI-82: not detected, BI-89: 0.0170, BI-90: 0.0242, WM-89: 0.0151, WM-90: 0.0132, WM-91: 0.0146, SW-91: 0.0110 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
PERFLUOROOCTANESULFONIC ACID (PFSA) | 256 ng/g ww | Liver concentration | Not Reported | Not Reported | 2 | Naples | Toxicity Factor Datasets | USA |
HEXACHLOROBENZENE | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | Toxicity Factor Datasets | USA | ||
DDE (2,4'-) | <5 ppm: 4, >5 ppm: 5 eggs/nest | Clutch size relative to DDE concentration | Embryo | 10 | Toxicity Factor Datasets | USA | ||
MERCURY COMPOUNDS | LCRS: 2.67, reference site: 0.30 µg/g ww | Blood concentration | Nestling | LCRS: 6, reference: 4 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 0.68, 2003: 0.71, 2004: 0.67 µg/g ww | Blood concentration | Not Reported | Nestling | 2002: 21, 2003: 32, 2004: 25 | Humboldt River | Toxicity Factor Datasets | USA |
METHYLMERCURY | 2002: 0.52, 2003: 0.57, 2004: 0.50 µg/g ww | Kidney concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
TRANS-NONACHLOR | MS-90: 0.0744, BI-82: 0.151, BI-89: 0.0290, BI-90: 0.166, WM-89: 0.0657, WM-90: 0.0677, WM-91: 0.0352, SW-91: 0.366 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
PERFLUOROOCTANESULFONIC ACID (PFSA) | 43 ng/g ww | Liver concentration | Not Reported | Not Reported | 1 | Bonita Springs | Toxicity Factor Datasets | USA |
MIREX | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | Toxicity Factor Datasets | USA | ||
<5 ppm: 81%, >5 ppm: 48% | Hatching success | Embryo | <5 ppm:27, >5 ppm: 29 eggs | Toxicity Factor Datasets | USA | |||
MERCURY COMPOUNDS | LCRS: 30.64, reference site: 7.77 µg/g ww | Feather concentration | Nestling | LCRS:14, reference: 14 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | See citation Table 3 | Blood chemistry | Not Reported | Nestling | See citation | Lahontan Reservoir & Humboldt River | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 0.93, 2003: 0.93, 2004: 0.70 µg/g ww | Brain concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
CIS-NONACHLOR | MS-90: 0.0233, BI-82: 0.103, BI-89: not detected, BI-90: 0.114, WM-91: not detected, SW-91: not detected µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
PCB | 0.08 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
<5 ppm: 95%, >5 ppm: 86% | Young survived 7-10 days | Embryo | <5 ppm:27, >5 ppm: 29 eggs | Toxicity Factor Datasets | USA | |||
MERCURY COMPOUNDS | LCRS: 0.54, reference site: 0.17 µg/g ww | Egg concentration | Embryo | LCRS: 26, reference: 42 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 14.2, 2003: 14.4, 2004: 15.2 g | Liver weight | Not Reported | Nestling | 2002: 2, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 0.23, 2003: 0.23, 2004: 0.19 µg/g ww | Brain concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
DIELDRIN | MS-90: 0.0258, BI-82: 0.0926, BI-89: 0.0270, BI-90: 0.0661, WM-89: 0.0308 WM-90: 0.0204, WM-91: 0.00887, SW-91: 0.0275 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
MERCURY (elemental) | 0.81 ± 0.50 µg/g dw | Feather concentration | Both Male and Female | Nestling | 10 | Georgia & South Carolina | Toxicity Factor Datasets | USA |
DDE (2,4'-) | 4.2 ppm ww | Egg concentration | Embryo | 10 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
<5 ppm: 0.232, >5 ppm: 0.201 mm | Embryo | <5 ppm:27, >5 ppm: 29 eggs | Toxicity Factor Datasets | USA | ||||
MERCURY COMPOUNDS | LCRS: 0.65 µg/g ww | Egg concentration | Embryo | 20 | Carson Lake & Lahontan Reservoir | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 12.8, 2003: 15.2, 2004: 13.0 g | Liver weight | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 20.45, 2003: 36.38 µg/g ww | Feather concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
DDD (4,4'-) | MS-90:0.0222, BI-82: 0.246, BI-89: 0.0180, BI-90: 0.0473, WM-89: 0.0168, WM-90: 0.0098, SW-91: 0.0683 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
METHYLMERCURY | Review, see citation Figure 2 | Egg concentration | Embryo | Not reported | Toxicity Factor Datasets | USA | ||
DDD (2,4'-) | 0.12 ppm ww | Egg concentration | Embryo | 4 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |
California Black Rail (Laterallus jamaicensis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY | See citation Figures 3 & 4 | Blood concentration | Both Male and Female | Not Reported | 64 | Gambinini Marsh, Mid-Petaluma Marsh, Black John Slough | Toxicity Factor Datasets | Sonoma | USA |
METHYLMERCURY | See citation Figures 3 & 4 | Feather concentration | Not Reported | 127 | Gambinini Marsh, Mid-Petaluma Marsh, Black John Slough | Toxicity Factor Datasets | Sonoma | USA |